Evidence map›Paper›PMID 41926824›Full record

ArticleMarine pollution bulletin2026

Differences in PFAS exposure between Pacific pinnipeds: The Galapagos (Zalophus wollebaeki) and California (Zalophus californianus) sea lions.

Ashley E Cave, Isabella G Livingston, Taylor M Gregory, Eleanor C Hawkins, Shelly Vaden, Marjorie Riofrío-Lazo, Diane Deresienski, Gregory A Lewbart, Anthony J Orr, Emily Griffith and 7 more

Abstract read
In one paragraph

Article in Marine pollution bulletin, 2026. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Not yet cited in PubMed.

0numbers the graph read from it
0cells of the map it votes in
0citing papers in PubMed
–field-weighted citation impact
1 · What the graph read from it

What it found

Each row is one number read from the abstract, on the scale the paper reported it, with its interval. Left of the dashed line favours the treatment, right favours the comparator. Under each row is the sentence it came from. New to these charts? A ten-minute tutorial.

The abstract states no effect estimate the extractor could read, or names no intervention and outcome on the map, so this paper lights no cell and moves no belief. It is still indexed, cited and linked below.

2 · The registry

The trial behind it

Trials whose registry record cites this paper, or whose number appears in the abstract. A trial that started after this paper was published is citing it as background, not reporting it.

Neither the registry nor the abstract names a trial number. If this is a trial report, that itself is worth knowing.

3 · Its place in the literature

Who cites it

0 citing papers in PubMed.

No citing paper in PubMed yet.

4 · The record

Corrections and comments

PubMed lists nothing against this paper. Absence here is not a guarantee, only a check that was made.

5 · Who and what money

Authors and funding

17 authors.

Ashley E CaveDepartment of Molecular Biomedical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States; Department of Clinical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States.
Isabella G LivingstonDepartment of Molecular Biomedical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States.
Taylor M GregoryGreensboro Science Center, Greensboro, North Carolina, 27455, United States.
Eleanor C HawkinsDepartment of Clinical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States.
Shelly VadenDepartment of Clinical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States.
Marjorie Riofrío-LazoGalapagos Science Center, Universidad San Francisco de Quito, Isla San Cristóbal, 200150, Islas Galapagos, Ecuador.
Diane DeresienskiDepartment of Clinical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States; Galapagos Science Center, Universidad San Francisco de Quito, Isla San Cristóbal, 200150, Islas Galapagos, Ecuador.
Gregory A LewbartDepartment of Clinical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States; Galapagos Science Center, Universidad San Francisco de Quito, Isla San Cristóbal, 200150, Islas Galapagos, Ecuador.
Anthony J OrrMarine Mammal Laboratory, Alaska Fisheries Science Center, National Marine Fisheries Service, National Oceanic and Atmospheric Administration, Seattle, Washington, 98115, United States.
Emily GriffithDepartment of Statistics, North Carolina State University, Raleigh, North Carolina, 27695, United States.
Christopher FullerU.S. Environmental Protection Agency, Office of Applied Science and Environmental Solutions, Research Triangle Park, North Carolina, 27711, United States.
Mark J StrynarU.S. Environmental Protection Agency, Office of Applied Science and Environmental Solutions, Research Triangle Park, North Carolina, 27711, United States.
James McCordU.S. Environmental Protection Agency, Office of Water, Research Triangle Park, North Carolina, 27711, United States.
Jacqueline BangmaU.S. Environmental Protection Agency, Office of Applied Science and Environmental Solutions, Research Triangle Park, North Carolina, 27711, United States.
Alissa C DemingThe Pacific Marine Mammal Center, Laguna Beach, California, 92651, United States.
Diego Páez-RosasGalapagos Science Center, Universidad San Francisco de Quito, Isla San Cristóbal, 200150, Islas Galapagos, Ecuador; Fundación Conservando Galapagos, Galapagos Conservancy, Isla Santa Cruz, 200350, Islas Galapagos, Ecuador; Dirección del Parque Nacional Galapagos, Unidad Técnica Operativa San Cristóbal, Isla San Cristóbal, 200150, Islas Galapagos, Ecuador.
Matthew BreenDepartment of Molecular Biomedical Sciences, North Carolina State University, Raleigh, North Carolina, 27607, United States; Comparative Medicine Institute, North Carolina State University, Raleigh, North Carolina, 27607, United States; Center for Human Health and the Environment, North Carolina State University, Raleigh, North Carolina, 27695, United States. Electronic address: mbreen3@ncsu.edu.

Funding

Translational Research Support CoreP30ES025128 · NIEHS · NORTH CAROLINA STATE UNIVERSITY RALEIGH · PI Sue Fenton · 2015 to 2026
$18.3M
Intramural EPA EPA999999NIEHS NIH HHS P30 ES025128
6 · The paper itself

Abstract

Per- and polyfluoroalkyl substances (PFAS) are a class of man-made persistent chemicals that have been detected in both terrestrial and aquatic environments and thus impact humans, household pets, agricultural species, and wildlife. PFAS exposure is linked to a variety of adverse health consequences, including cancer and immune disruption. This study investigates differences in PFAS exposure between California (CSL, n = 69) and Galapagos (GSL, n = 65) sea lion pups and juveniles across various sampling locations within each species' habitat range. Whereas the GSL were all considered healthy, 17 of the 69 CSL were classified as malnourished. Comparing the two species, significantly higher serum concentrations of summed PFAS, perfluorooctanesulfonic acid (PFOS), perfluorononanoic acid (PFNA), and perfluorodecanoic acid (PFDA) were detected in CSL than in GSL. This elevated PFAS exposure in CSL is likely related to historic pollution in their environment and close proximity to the urbanized coastline of Southern California. Within species, malnourished CSL had significantly higher PFNA than healthy CSL pups. GSL pups also tended to have higher PFAS levels than GSL juveniles. Within the Galapagos archipelago, PFAS exposure differed between rookeries, with PFOS exceeding its method reporting limit (0.5 ng/mL) in every sample, including GSL from islands uninhabited by humans. Summed PFAS, PFNA, PFDA, and perfluoroundecanoic acid (PFUnA) were all significantly higher in sea lions sampled on uninhabited than inhabited islands in the Galapagos archipelago. This study is the first comprehensive report of PFAS in CSL and the first archipelago-wide assessment of PFAS in GSL.

Indexed as

CaniformiaEnvironmental MonitoringFluorocarbonsSea LionsWater Pollutants, ChemicalAlkanesulfonic AcidsAnimalsCaliforniaAlkanesulfonic AcidsFluorocarbonsWater Pollutants, ChemicalCalifornia sea lion (Zalophus californianus)Endangered speciesGalapagos sea lion (Zalophus wollebaeki)Marine pollutionPer- and polyfluoroalkyl substances (PFAS)

Identifiers

PMID41926824
PMCPMC13392999

What OpenQuestion holds

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LicenceCC BY
Read underepoch 390

Registered trials

None linked

Read under generation 80e0d062 · epoch 390. Bibliography from PubMed, PubMed Central and OpenAlex; grants from NIH RePORTER; trial links from ClinicalTrials.gov; estimates, votes and beliefs from the OpenQuestion graph.